EN 13592:2017

2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.Kunststoffsäcke für die Abfallsammlung aus Haushalten - Typen, Anforderungen und PrüfverfahrenSacs en plastique pour la collecte des déchets ménagers - Types, exigences et méthodes d'essaiPlastics sacks for household waste collection - Types, requirements and test methods55.080Sacks. Bags13.030.40Naprave in oprema za odstranjevanje in obdelavo odpadkovInstallations and equipment for waste disposal and treatmentICS:Ta slovenski standard je istoveten z:EN 13592:2017SIST EN 13592:2017en,fr,de01-september-2017SIST EN 13592:2017SLOVENSKI
STANDARDSIST EN 13592:2003+A1:2008/AC:2008SIST EN 13592:2003+A1:20081DGRPHãþD

EUROPEAN STANDARD NORME EUROPÉENNE EUROPÄISCHE NORM
EN 13592
February
t r s y ICS
w wä r z r Supersedes EN
s u w { tã t r r u ªA sã t r r yEnglish Version
Plastics sacks for household waste collection æ Typesá requirements and test methods Sacs en plastique pour la collecte des déchets ménagers æ Typesá exigences et méthodes d 5essai
Kunststoffsäcke für die Abfallsammlung aus Haushalten æ Typená Anforderungen und PrüfverfahrenThis European Standard was approved by CEN on
t s November
t r s xä
egulations which stipulate the conditions for giving this European Standard the status of a national standard without any alterationä Upætoædate lists and bibliographical references concerning such national standards may be obtained on application to the CENæCENELEC Management Centre or to any CEN memberä
translation under the responsibility of a CEN member into its own language and notified to the CENæCENELEC Management Centre has the same status as the official versionsä
CEN members are the national standards bodies of Austriaá Belgiumá Bulgariaá Croatiaá Cyprusá Czech Republicá Denmarká Estoniaá Finlandá Former Yugoslav Republic of Macedoniaá Franceá Germanyá Greeceá Hungaryá Icelandá Irelandá Italyá Latviaá Lithuaniaá Luxembourgá Maltaá Netherlandsá Norwayá Polandá Portugalá Romaniaá Serbiaá Slovakiaá Sloveniaá Spainá Swedená Switzerlandá Turkey and United Kingdomä
EUROPEAN COMMITTEE FOR STANDARDIZATION COMITÉ EUROPÉEN DE NORMALISATION EUROPÄISCHES KOMITEE FÜR NORMUNG
CEN-CENELEC Management Centre:
Avenue Marnix 17,
B-1000 Brussels
t r s y CEN All rights of exploitation in any form and by any means reserved worldwide for CEN national Membersä Refä Noä EN
s u w { tã t r s y ESIST EN 13592:2017

Sampling . 28 Annex C (informative)
Template for reporting test results . 30 Annex D (informative)
Typical characteristics of biodegradable/compostable films for caddy liners . 34 Bibliography . 35 SIST EN 13592:2017

Í
x where x is the minimum value of: ttNN+2515or 0,35Nt,
as 1
as 2
as 2
7.1.3.3 Average values The arithmetic average value of the film thickness, calculated according to either 7.2.3.2 or 7.2.3.3, shall be: a) > Nt –5 %, when Nt > 20 m; b) > Nt –8 %, when Nt
¶ 20 m. 7.1.4 Opacity 7.1.4.1 General Unless otherwise specified, the individual and average values of the opacity shall be in accordance with 7.1.4.2 and 7.1.4.3. No defective sack shall be permitted out of 10 sacks (or strips) for individual values of each sack (or strip) and the average value of the 10 measurements when tested according to 7.2.4.1. SIST EN 13592:2017

¶ 55 % for household waste collection sacks; b)
· 45 % for household selective waste collection sacks. 7.1.4.3 Average value The arithmetic average value of the opacity calculated for 10 measurements shall be: a)
· 60 % for household waste collection sacks; b)
¶ 40 % for household selective waste collection sacks. 7.1.5 Resistance to leakage No defective sack shall be permitted out of five sacks when tested according to 7.2.5. 7.1.6 Drop impact resistance 7.1.6.1 Sacks for household waste collection No more than three defective sacks shall be permitted out of 20 sacks when tested according to 7.2.6. If this requirement is not satisfied, then 10 additional sacks shall be tested according to 7.2.6 and in total no more than five defective sacks out of the 30 sacks shall be permitted. 7.1.6.2 Sacks for selective waste collection Unless otherwise specified in an agreement between the supplier and the customer specifying different test loads, the test loads given in Table 2 shall be applied. No more than three defective sacks shall be permitted out of 20 sacks when tested according to 7.2.6. If this requirement is not satisfied, then 10 additional sacks shall be tested according to 7.2.6 and in total no more than five defective sacks out of the 30 sacks shall be permitted. 7.1.7 Resistance of the closing device 7.1.7.1 Tensile strength of ties For sacks provided with an integrated or added tie, the tensile strength of the tie when measured according to 7.2.7.1 shall not be less than 40 N. No more than one failure out of the 10 ties tested is permitted. When the ties are not integrated to the sacks, the number of ties shall not be less than the number of sacks. 7.1.7.2 Resistance of the closing system of drawtight sacks No more than two defective sacks out of 10 shall be permitted when tested according to 7.2.7.2. For sacks for selective waste collection if there is an agreement between the supplier and the customer specifying different test loads (see 7.1.6.2), these agreed test loads shall be applied. In the absence of an agreement between the supplier and the customer, the test loads according to Table 3 shall be applied. SIST EN 13592:2017

7.2.3.3 Gravimetric method Cut out one strip of (100 ± 0,5) mm width from each of the five sacks from Group V, in the transversal
direction and in the middle of the sack. Measure the length li of each strip by using the rule. Calculate the total length of the five strips, lt. Weigh together the five strips pt with the balance. Calculate the average value of the film thickness, t, by using the following formula: ttpltρ××=0001,01 where t is the average film thickness, in micrometres; lt is the total length of the five strips, in millimetres; pt is the weight
of the five strips, in grams;
is the density of the film material, expressed in grams per cubic centimetres. SIST EN 13592:2017

Key 1 variable power supply 2 photoelectric cell 3 plastic film test specimen 4 light meter 5 matt black base of (3 ± 0,5) cm thickness 6
matt black diagram of (1 ± 0,1) cm diameter Key 1 variable power supply 2 photoelectric cell 3 plastic film test specimen 4 light meter 5 matt black base
a) Reference apparatus b) Other apparatus Figure 1 — Typical apparatus for the control of opacity 7.2.4.1.3 Procedure This test shall be performed using 10 strips, 100 mm minimum wide, cut from each of the 10 sacks from Group I in the same way as for those for the thickness test, avoiding printed areas as far as possible. Turn on the light source and wait 5 min for the stabilization of the light. Set up the light, using the variable power supply, to an illuminance, as measured by the photo electric cell, such that lo = 1 000 lx. Place the test specimen with the inner side of the sack on the cell and record the illuminance of the transmitted light, l1, looking for: a) for household waste collection and pre-collection sacks, the lowest value over the entire area of the test specimen; b) for household selective waste collection sacks, the highest value over the entire area of the test specimen. Express the result as a percentage, rounded to the nearest integer. For example, for a value of 38,5 %, the result is 39 %. Repeat the procedure for each sack. SIST EN 13592:2017

Volume l
P
¶ 400 and L
¶ 400 400
¶ P
¶ 520 and 400
¶ L
¶ 700 P > 520 or L > 700 Tap water 2 3 6 Mixture of water and saw dust (50/50 in volume) 2 3 6 7.2.5.2 Procedure When sacks are supplied with a tie sealed to the sack, the tie shall not be removed before performing this test. Pour into a sack 2 l, 3 l or 6 l of water, as applicable (see Table 1). Hang up the sack by the top to the support and monitor the sack for 5 min, for any evidence of leak. If a drop leaks within these 5 min, start counting the number of drops, n, escaping from the sack during 1 min: a) If n is less than or equal to 20, the sack is declared “conform”; b) If n is greater than 20, proceed with the second step, using the same sack. Prepare 2 l, 3 l or 6 l, as applicable (see Table 1) of the wet mixture, as defined in 7.2.5.1.3. Pour the volume of the wet mixture in the sack. Hang up the sack by the top to the support and monitor the sack for 5 min, for any evidence of leak. Count the number of drops, n, if any, escaping from the sack during 1 min. If n is less than or equal to 20, the sack passes is declared “conform”. If n is greater than 20 or if all water escaped during the first 5 min, the sack is declared “non-conform”. Repeat the procedure for each sack. SIST EN 13592:2017
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